orange county – report of waste discharge · 2014-07-02 · making traditional pollutant control...
TRANSCRIPT
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July 1, 2014
Orange County – Report of Waste Discharge
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Landscape Change
20% Interflow
40% Infiltration
10% Surface Flow
30% Evapotranspiration
5% Interflow
5% Infiltration
15% Evaporation
75% Surface Flow to Pipes
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Stormwater and Land Use Change
There are four interrelated but separable effects of land-use changes on the hydrology of an area: changes in peak flow characteristics, changes in total runoff, changes in quality of water, and changes in the hydrologic amenities.
Luna Leopold, 1968
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Municipal Stormwater Permits The federal Clean Water Act requires that stormwater permits for discharges from municipal storm sewers: • may be issued on a system- or jurisdiction-wide basis; • shall include a requirement to effectively prohibit non-stormwater
discharges into the storm sewers; and • shall require controls to reduce the discharge of pollutants to the
maximum extent practicable, including management practices, control techniques and system, design and engineering methods, and such other provisions as the Administrator or the State determines appropriate for the control of such pollutants.
1990 1996 2003 2009 2014
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Report of Waste Discharge
Introduction State of the Environment
• Bacteria • Nutrients • Toxicity • Total Dissolved Solids
Controlling Pollutant Sources – Countywide Programs
Controlling Pollutant Sources - Watershed Programs Program Development Recommendations
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State of the Environment
Four key questions: • Is our water safe to drink? • Is it safe to swim in our waters? • Is it safe to eat fish and shellfish from our
waters? • Are our aquatic ecosystems healthy?
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Prioritization
• Raw exceedance frequencies provide only partial information
• CCME water quality index1 integrates Percent of indicators with exceedances Percent of measurements/tests with exceedances Magnitudes of exceedances
Index produces a score from 0 – 1 (or 0 – 100) with higher scores reflecting lower overall exceedances
Used widely (e.g., Central Coast Regional Board) 1 Canadian Council of Ministers of the Environment . 2001. Canadian water quality guidelines for the protection of aquatic life: CCME Water Quality Index 1.0, Technical Report. In: Canadian environmental quality guidelines, 1999, Canadian Council of Ministers of the Environment, Winnipeg.
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CCME Index
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BACTERIA
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Bacteria: Report Card Grades
Beach report card grades
consistently high in dry weather
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Bacteria: Beach Closures
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Bacteria: Beach Advisories
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Bacteria: Sanitary Sewer Overflows
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Bacteria: CASC
Incident Triggering CASC Activation Receiving Waters Date Type Volume Diverted to Sanitary Sewer (Gallons)
Sanitary sewer force main rupture Tijeras Creek/San Juan Creek/Doheny Beach March 23, 2010 SSO (public) 2,500,000
Mobile home community, Lake Forest Aliso Creek June 25, 2010 SSO (private) 2,400
Sanitary sewer force main rupture Buck Gully Creek/Little Corona Beach July 2 , 2010 SSO (public) 710,000
Manufacturer corporate HQ, Irvine Peters Canyon Channel January 13, 2011
Other (fountain discharge) 100,000
Residential apartment complex, Anaheim Santa Ana River April 12, 2012 SSO (private) 1,900
Residential apartment complex, Anaheim Santa Ana River April 18, 2012 SSO (private) 77,500
Packaging products manufacturer, Buena Park
Fullerton Creek/Coyote Creek/San Gabriel River July 25, 2012 Other (clarifier
discharge) 355,000
Ammonia refrigeration leak, Santa Ana Santa Ana Delhi Channel February 4, 2013
Other (ammonia discharge) 200
Industrial chemical facility fire, Santa Ana Greenville-Banning Channel
August 28, 2013
Other (fire suppression runoff) ~3,000,000
Sanitary sewer pump station failure, Newport Beach
Santa Ana-Delhi Channel/Upper Newport Bay
August 31, 2013
SSO (public, mixed with channel water) 45,000
Hotel facility HVAC system discharge Lane Channel December 16, 2013
Other (HVAC discharge w/ dye) 140,000
Total: 6,932,000
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Bacteria: Dry Weather Diversions
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Bacteria: Wet Weather Challenges
Poorer conditions Larger flows Potential for new
methods • Wet weather
epidemiology study • Source tracking tools,
including for in situ virus detection
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Bacteria: TMDL Programs
Bacteria TMDL Programs • Seeing significant dry weather progress through
BMPs and water conservation/flow reduction efforts • Focus shifting to isolate source of remaining dry
weather exceedances and on wet weather load reductions Watershed Special Studies
– Comprehensive Load Reduction Plan (CLRP) BMP Effectiveness Study
– Microbial Source Tracking
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• 1000ft of existing rock/earthen channel dredged and widened and revegetated with native plants
Bacteria: CLRP BMP Effectiveness Study
Horno Retarding Basin (2003) • Designed to reduce peak flows
from ~1,800 acres of the Ladera Ranch Planned Community
• Includes Water Quality Detention Basin (~8 acres) to treat dry weather and first-flush flows (up to 265 cfs)
Narco Channel Restoration (2005)
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Bacteria: CLRP BMP Effectiveness Study
BMP Effectiveness - Bacteria Reductions (Enterococci)
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Bacteria: Summary
BMPs and overall flow reductions resulting in significant reductions in dry weather
Successful dry weather bacteria BMPs appear ineffective in providing meaningful wet weather reductions
Microbial source tracking may be useful tool assist with isolating remaining bacteria sources causing exceedances
Overall reduction in the number of sewage spills correlates with lower number of beach closures and increased recreational water use. (Countywide Area Spill Control Program – CASC)
Decrease in the total number of beach mile days posted due to AB411 standards violations has increased beneficial use. Example: Doheny
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NUTRIENTS
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Nutrients: A Regional Problem
Exceedances widespread Algal overgrowth less so but occurs in
undeveloped areas as well May contribute to harmful algal blooms
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Nutrients: Summary
Nonpoint and diffuse sources such as leaching from upland soils and intrusions from shallow groundwater are increasingly important.
Nutrients can be readily transported in and out of various reservoirs (e.g., sediments, groundwater) and undergo complex biological transformation and cycling, making traditional pollutant control strategies less effective for nutrients.
Improved management strategies may contribute to further progress, particularly in streams and channels, by accounting for site-specific conditions, promoting Low Impact Development, and accounting for broader regional sources.
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TOXICITY
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Regional Toxicity Patterns
Toxicity widespread but sporadic and at low levels No apparent trends over time
% Stream Miles
Ceriodaphnia Survival
Open Urban
Toxic 2.1 2.4
Nontoxic 97.9 97.6
% Stream Miles
Ceriodaphnia Reproduction
Open Urban
Toxic 63.0 37.4
Nontoxic 37.0 62.6
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Pesticides Most Likely Cause
TIEs and other studies point to pesticides
Use patterns are dynamic
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Source Control: Pesticides Summary of Toxicity - California Watersheds – SWRCB – 2010
• Of the 992 sites,48% had at least 1 sample which exhibited toxicity
• With the exception of ammonia, all evaluations implicated pesticides, primarily OPs and more recently pyrethroids.
Analysis by U.C. Davis of new DPR rule making suggests that the regulations will largely--but not completely--end widespread water and sediment toxicity from pyrethroids in California's urban watersheds (Kelly Moran pers.comm.).
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Toxicity: Summary
Pesticides are contributing to chronic toxicity; Need to improve information on pesticide use. Support source control approaches. Metals are not an issue. Geochemistry.
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DISSOLVED SOLIDS
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DISSOLVED SOLIDS: PRIMARY ISSUES
Persistent and widespread exceedances of total dissolved solids occur in channels and at discharge outfalls.
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DISSOLVED SOLIDS: SUMMARY
Natural sources in regional groundwater represent a large portion of elevated dissolved solids.
Understanding local geology is key to understanding sources of dissolved solids and the pathways they travel in the watershed.
While the flood control system provides one pathway for dissolved solids in groundwater to reach the surface, other natural pathways (such as artesian springs) exist and there is evidence of historically elevated dissolved solids levels in surface water in the region.
Determine significance of TDS as a stressor. Investigate feasibility of mass balance study.
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DRY WEATHER RECONNAISSANCE & ID/IC
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ID/IC Complaints & Enforcement
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Dry Weather Reconnaissance: NALs
NALs vs. Als (Dry Weather) Table 3.7.1. Comparison of the 2011-12 NALs Data with the Weather Hybrid Reconnaissance Monitoring Program Data for the 2009-10 Reporting Period
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Dry Weather Reconnaissance: Summary
NALs Program Summary: • The current NALs program has made achievements in
reducing anthropogenic sources of NALs constituents, but lacks the flexibility to re-prioritize sites or reach definitive endpoints.
• Source investigation resources are therefore confined to a limited number of outfall sites Countywide.
• Groundwater, geologic conditions, and other related discharge sources are an ongoing challenge to meeting the NALs utilizing the current Basin Plan Objectives.
• The current NALs program does not account for evaluating impacts to receiving waters, which could be utilized in a potential site prioritization program.
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Dry Weather: Recommendation
NALs Program Summary: • Reinstate Dry Weather Reconnaissance Program
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Hydromodification
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Hydromodification
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Hydromodification: Recommendation
Implement an approach to hydromodification that is (pre)informed by a watershed analysis and channel-specific protection goals.
Pending completion of the analysis, land development projects discharging to engineered channels are exempted from requirements.
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LID Hierarchy
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Runoff Retention - Soils
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LID Hierarchy: Recommendation
Incorporate Integrated Water Resource Management (IRWM) element into land planning.
Modify LID Hierarchy to establish equivalency of “On-Site BMP” and “Off-Site BMP” solutions.
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Receiving Water Limitations (RWL)
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RWL: Recommendation
A.1 Discharge Prohibition
A.2 Receiving
Waters Limitation
B.3.c Compliance
Option
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Questions (?)